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First records of the sponge crab Dromia personata (Brachyura) in the Netherlands and its historical findings in the North Sea

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Only a few records exist of the sponge crab Dromia personata in the North Sea. Most records are in local languages, and have limited availability. On 11 August 2016, D. personata was found by divers in the Eastern Scheldt, a former estuary in the south-western part of the Netherlands. In the months to follow, at least four other individuals were observed by divers at the same and nearby locations. This paper lists these and former records in the North Sea. The distribution pattern, and the possible migration of the sponge crab in relation to environmental conditions such as seawater temperature are discussed, as well as the crab’s use of the non-native sponge Celtodoryx ciocalyptoides.
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M A R I N E R E C O R D Open Access
First records of the sponge crab Dromia
personata (Brachyura) in the Netherlands
and its historical findings in the North Sea
Godfried W. N. M. van Moorsel
1*
, Floris P. Bennema
2
and Reindert Nijland
3
Abstract
Only a few records exist of the sponge crab Dromia personata in the North Sea. Most records are in local languages,
and have limited availability. On 11 August 2016, D. personata was found by divers in the Eastern Scheldt, a former
estuary in the south-western part of the Netherlands. In the months to follow, at least four other individuals were
observed by divers at the same and nearby locations. This paper lists these and former records in the North Sea. The
distribution pattern, and the possible migration of the sponge crab in relation to environmental conditions such as
seawater temperature are discussed, as well as the crabs use of the non-native sponge Celtodoryx ciocalyptoides.
Keywords: Sponge crab, Dromia personata, North Sea, Southern species, Distribution expansion
Background
Geographic distribution: Dromia personata (Linnaeus,
1758) is known from the Mediterranean Sea, and in the
East Atlantic Ocean from Western Sahara, Ascension,
Azores and Canary Islands, north to Anglesey (Wales),
the Clyde Sea (Scotland) and the English Channel. North
Sea records are rare (see below and Fig. 1). Records from
São Tomé, Senegal, Cabo Verde and Madeira and pos-
sibly also St. Helena refer to Dromia marmorea Forrest,
1974 (Christiansen 1969; Manning and Holthuis 1981;
Wolff 2002; Ashton et al. 2017; Allen 1967; González
2016; González et al. 2017; Araújo and Wirtz 2015; De
Grave et al. 2017). Morphological differences between D.
personata and D. marmorea are discussed in Manning &
Holthuis (1981). In British waters, the sponge crab has
been recorded infrequently. In Ireland, the first speci-
mens of D. personata were caught only recently, in 2010
and 2011 (Quigley and O'Donovan 2013).
Only a few records of sponge crabs from the North
Sea exist (Fig. 1). In 1824, two specimens were found at
Billingsgate Market (London) among oysters from Whit-
stable Bay (Anonymous 1824); this was the first record
from the United Kingdom (Bell 1853). Another speci-
men was caught in 1880 in deep water of the open sea
off the Belgian coast (Pelseneer 1881). In 1912, D. perso-
nata was caught in the vicinity of the Galloperlight
vessel off the Essex coast (Patterson 1913). Leloup
(1941) lists a record from 1937 near the Sandettie Bank
at 1920 fathoms (3537 m). This bank lies north of
Calais, in what is now the French part of the North Sea.
A footnote in Leloup (1941) mentions two more speci-
mens, also from 1937, caught at the White Bank, the
now submerged west bank of the Elbe glacial valley. Al-
though this area is 170 km west of Denmark, it lies just
east of 6° latitude, and was therefore considered to be-
long to the Danish fauna (Wolff 2002). The rectangular
area specified in Leloup (1941) presently lies in the Ger-
man part of the North Sea (Fig. 1) and is roughly equi-
distant from the Dutch, German and Danish coast. The
designation of the latitude in the footnote in Leloup
(1941) in multiples of 15suggests a possible error in
the eastern longitude: it is probably not E 6°3but E 6°
30. This also better fits the location of the White Bank,
at approximately N 55°10and E 6°10. The last speci-
fied site in the North Sea, in 1953, is the Fairy Bank
(Adema 1981) in the French part of the North Sea. In
addition, Ingle (1983) mentions the Wash and Thames
as North Sea locations. The latter record is possibly also
included in Adema (1991), which shows three locations
at the English North Sea coast, off Kent and Norfolk.
Leloup & Gills (1965) report D. personata from shrimp
* Correspondence: vanmoorsel@ecosub.nl
1
ecosub, P.O. Box 126, 3940 AC Doorn, The Netherlands
Full list of author information is available at the end of the article
© The Author(s). 2017 Open Access This article is distributed under the terms of the Creative Commons Attribution 4.0
International License (http://creativecommons.org/licenses/by/4.0/), which permits unrestricted use, distribution, and
reproduction in any medium, provided you give appropriate credit to the original author(s) and the source, provide a link to
the Creative Commons license, and indicate if changes were made. The Creative Commons Public Domain Dedication waiver
(http://creativecommons.org/publicdomain/zero/1.0/) applies to the data made available in this article, unless otherwise stated.
van Moorsel et al. Marine Biodiversity Records (2017) 10:28
DOI 10.1186/s41200-017-0129-7
catches during 19491964, in a 25 km long strip inside
the 5-mile (9 km) zone from the Belgian coast between
Middelkerke and Wenduine. They call the crab as being
assez rare, the one but lowest of their four abundance
categories, which suggests the catch of at least several
specimens. Coordinates of the above-mentioned historic
North Sea records are listed in Table 1.
Methods
New records in the Netherlands emerged by observa-
tions made via SCUBA diving. The first Dutch record
of Dromia personata was posted on 16 August 2016 on
the internet (NatureToday.com) and prompted other
biologists and diving naturalists to search for the spe-
cies. This resulted in findings that were sometimes ac-
companied by underwater photos (Fig. 2) or video. As
such, this paper shows the valuable contribution of citi-
zen science (Thiel et al. 2014). Due to its sponge cover
D. personata is well camouflaged, but once found it
was easily recognized and could not be confused with
other brachyurans.
Results
In 2016, several individuals of Dromia personata were
found in the Eastern Scheldt, and these constituted
the first records in the Netherlands. One was found
on 11 August 2016, and was taken from its location
(Zeelandbrug: 51° 3744N, 3° 5449E). Subse-
quently, at least 12 times between 14 August and 30
October 2016, D. personata was recorded (but not
collected) again at the same location. The maximum
number of sponge crabs observed per dive was two.
Consequently, a minimum number of three individ-
uals must have been present at the Zeelandbrug. The
relatively high number of records at this location may
reflect the popularity of this dive site. In addition,
two more sponge crabs were found in the Eastern
Scheldt, at Strijenham (51° 3117N, 4° 0828E)
and Goesse Sas (51° 3232N, 3° 5552E). Con-
sideringthedistancebetweentheselocationsandthe
timing it is highly unlikely that these records repre-
sented the same individuals. Therefore, a total of at
least five sponge crabs must have been present in the
Eastern Scheldt in 2016.
Fig. 1 Records of Dromia personata in the southern North Sea. Locations of records in the southern North Sea with boundaries of national
continental flats and year of catch or observation where available. Grey symbols from Adema (1991). Left part of rectangle in the German part of
the North Sea is the area of two catches in 1937 as mentioned in Leloup (1941); whole rectangle (including interrupted line) is probable area of
occurrence (see text)
van Moorsel et al. Marine Biodiversity Records (2017) 10:28 Page 2 of 5
Table 1 Dromia personata. Historic catches and recent observations in the North Sea
Date Name in reference Location Depth n Sex Carapace width
(x length)
Reference Co-ordinate Remark
NE
1824 D. mediterranea,
Leach
Whitstable Bay Anonymous
1824
Found among Oysters from
Whitstable Bay at Billingsgate
market, London.
Communicated by Mr. J.E. Gray
and presented at June 22, 1824
1880 D. vulgaris Edw. deep water in open sea off
the Belgian coast
deep 1 almost
110 mm
Pelseneer
1881
??
late Dec. 1912 D. vulgaris Galloperlight-vessel Patterson
1913
51° 43,9001° 57,8Taken by the Lowestoft
sailing-trawler Giralda, skipper
J. Stead.
Specimen presented by Mr.
F.C. Cook. Co-ordinate from
internet
2905-1937 D. vulgaris Milne
Edwards
Sandettie bank (SW-end) 1920 fathom
=3537 m
150 × 40 mm Leloup 1941 51° 1130001° 52Dredged. Sandettie Bank rises
up to 20 m, so catch must
have been next to this bank.
Specimen presented by Cyriel
Pecceu, Nieuwpoort
June 1937 D. vulgaris Milne
Edwards
White Bank ~30 m 2 40 × 35 &
85 × 65 mm
Leloup 1941
footnote
NW 55° 15
SE 54° 30
006° 00
006° 3
Reported by letter 22 June,
1937 by Cyriel Pecceu,
Nieuwpoort
1949 to 1964 D. vulgaris H. Milne-
Edwards
within 5 nautical miles from
the Belgian coast between
Middelkerke & Wenduine
>1? Leloup and
Gilis 1965
Bycatch experimental shrimp
fishery.
abundance cat. (3) = assez
rare
1612-1953 D. personata
(Linnaeus, 1758)
approximately near Fairy
bank
1Adema 1981,
1991
NW 51° 2400
SE 51° 2110
002° 1830
002° 2210
In collection Royal Belgian
Institute of Natural Sciences,
Brussels
?D. personata
(Linnaeus, 1758)
2 locations Kent coast and
1 location Norfolk coast
Wash and Thames
Adema 1991:
map 1
Ingle 1983
1108 to 3010
2016
D. personata
(Linnaeus, 1758)
16 records at 3 location in
Eastern Scheldt,
Netherlands
313 m 5&~ 55 mm this study see text
0904 to 0208
2017
D. personata
(Linnaeus, 1758)
3 records at 2 location in
Eastern Scheldt,
Netherlands
47m 2 this study see text
van Moorsel et al. Marine Biodiversity Records (2017) 10:28 Page 3 of 5
In 2017, at least two individuals of Dromia personata
were sighted in the Eastern Scheldt. On 9 April, a mori-
bund sponge crab without cover was found at the Zee-
landbrug and on 27 July and 2 August, a sponge crab
was seen at Schelphoek (51° 4102N, 003° 4907E).
This indicates that the local occurrence is not limited to
a single-season event.
The carapace width of the first crab found was
55 mm, and the other crabs were of similar size. Both
sexes were encountered; the females were non-
ovigerous. In 2016, all sponge crabs were found with a
cover of either the native sponge Halichondria panicea,
or the non-indigenous sponge Celtodoryx ciocalyptoides.
The crab of 27 July 2017 carried the soft coral Alcyo-
nium digitatum on its back. As far as we know, only
sponges and tunicates have been recorded as natural
cover material. Therefore, this is the first case of a
sponge crab with an alcyonacean cover. During the 2016
recording period, seawater temperature was 20 °C in
August, dropping to 13 °C at the end of October.
The 2016 and 2017 Dutch records are summarized
in Table 1. Detailed information is provided in
Additional file 1.
Discussion
Almost 200 years after the first record of Dromia perso-
nata in the North Sea, about 10 records are known from
this continental sea. Approximate coordinates of catch
locations could be deduced from the literature for only 4
specimens, the last one from 1953, which is 63 years be-
fore the present records. The discovery of at least 5 indi-
viduals, both males and females, at three locations in the
Eastern Scheldt in 2016 constitutes a relatively large
addition to both the number of records and the total
number of individuals.
Considering the rarity of this species in the North Sea,
finding at least 5 sponge crabs in such a short time
frame is remarkable. On the other hand, finding several
individuals within 1 year has happened before: in 1824
two specimens were found, and in 1937 3 specimens
were reported. In Ireland, the first two specimens were
found only 8 months apart in 2010 and 2011 (Quigley
and O'Donovan 2013). Possibly, this species shows rapid
expansions in certain years only.
Because Dromia personata is a Lusitanian species that
reaches the limit of its northern distribution in the
southern North Sea, its presence may be expected in
years with high water temperatures. In recent decades,
seawater temperatures have increased in the area and
several species have demonstrated a northward shift in
distribution (van der Kooij et al. 2016; Franke and
Gutow 2004; Hiscock et al. 2004). Therefore, the chance
of encountering the sponge crab in the Netherlands may
also be increasing. This possibility is supported by other
northern records of D. personata in the last decade: the
first two Irish records (Quigley and O'Donovan 2013),
and an increased occurrence in the Bristol Channel
(Ashton et al. 2017).
Moreover, environmental conditions in the Eastern
Scheldt may increasingly favour the presence of this spe-
cies. In 1986, the Eastern Scheldt barrier was completed.
This still allows a tidal regime, but tidal currents are di-
minished and light attenuation is decreased. The hard-
substratum ecosystem has changed dramatically, notably
due to the alien Japanese oyster Magallana gigas. Also,
sponges and tunicates, used as camouflage by the sponge
crab, are now omnipresent. Sponge crabs were observed
not only bearing the native breadcrumb sponge Hali-
chondria panicea but also the non-native sponge Celto-
doryx ciocalyptoides. In recent years, thick layers of C.
ciocalyptoides have developed into one of the most
abundant sponges in the Eastern Scheldt (pers. obs.).
Therefore, this sponge offers a favourable resource for
crabs in search of cover material.
The distribution of Dromia personata suggests migra-
tion into the North Sea from the English Channel, either
as larvae or as adults. As the last two pairs of the crabs
pereiopods are used for sponge-attachment, only two pairs
of legs are used for locomotion. Although D. personata is
able to walk at considerable speed over short distances if
necessary (pers. obs.), its capacity to walk over long dis-
tances, for example from the English Channel to the East-
ern Scheldt, is probably limited. The importance of larval
transport should therefore not be underestimated. In re-
cent years, several wind farms have been built in the Bel-
gian part of the North Sea. The seabed around the wind
turbines has been covered with stones. Perhaps these areas
are used for settlement of sponge-crab larvae. As such,
they may function as stepping stones between the English
Channel and the Eastern Scheldt. However, underwater
observations and catches, preferably of juveniles, have not
yet been made to confirm this.
Fig. 2 Dromia personata in situ, 6 October 2016, Zeelandbrug,
Eastern Scheldt. Underwater photo by Mick Otten
van Moorsel et al. Marine Biodiversity Records (2017) 10:28 Page 4 of 5
Finally, the appearance of the sponge crab may also be
related to accidental introduction via mariculture, but this
scenario is considered unlikely, due to absence or rarity in
donor areas, and probably low survival during transport.
Conclusions
At least five individuals of Dromia personata were found in
the Eastern Scheldt in the Netherlands in 2016 and 2017.
These findings extend the known distribution range of this
crab species and suggest a sudden increase in abundance.
Additional file
Additional file 1: Sponge crab (Dromia personata): Observations in the
Eastern Scheldt, Netherlands, in 2016 and 2017. (XLSX 22 kb)
Acknowledgements
We would like to thank Glen Biscop, Marianne Ligthart, Marco Vinke, Carl
Verlinde, Martin Gruson, Stefan Verheyen, René van Zweden, Lilian
Schoonderwoerd, Paul & Maria Engels, Krisna Wouters, Mick Otten, Hans
Vulink, Maurits van Kosteren and Astrid Vis for providing data and agreeing
to its use in this manuscript. Furthermore, we thank Danny Eibye-Jacobsen,
who kindly provided a pdf of Wolff 2002. We gratefully acknowledge the
help of Susan Hewitt in checking writing style, spelling and grammar.
Funding
This study was self-funded.
Availability of data and materials
All data generated or analysed during this study are included in this published
article and its supplementary information files.
Authorscontributions
FB and GvM made the initial observation leading to this report. GvM, FB and
RN collected further observations, analysed the data and wrote the manuscript.
All authors read and approved the final manuscript.
Authorsinformation
GvM is an independent marine ecologist and consultant. FB is a biologist
focussing on marine ecology and research of historic data to reconstruct the
composition of marine communities before intensive fisheries took their toll.
RN is a molecular microbiologist at the Marine Animal Ecology group at
Wageningen UR, with a strong interest in Dutch crustaceans. All three authors
are avid scuba-divers and have logged hundreds of hours underwater in Dutch
coastal waters.
Ethics approval and consent to participate
Not applicable
Consent for publication
All persons contributing to this manuscript have consented that their data
and personal details will be published.
Competing interests
The authors declare that they have no competing interests.
PublishersNote
Springer Nature remains neutral with regard to jurisdictional claims in
published maps and institutional affiliations.
Author details
1
ecosub, P.O. Box 126, 3940 AC Doorn, The Netherlands.
2
Vincent van
Goghstraat 88, 8932 LK Leeuwarden, The Netherlands.
3
Marine Animal
Ecology Group, Wageningen University, P.O. Box 338, 6700 AH Wageningen,
The Netherlands.
Received: 4 August 2017 Accepted: 30 October 2017
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The field of citizen science is flourishing, and although terrestrial projects are more visible, in recent years thousands of volunteers have actively participated in marine research activities. These volun-teers (also termed 'citizen scientists') may have experience in the research in which they are par-ticipating, but they have no formal degree in marine science or related topics. The participation of large numbers of volunteers with variable educational or professional backgrounds poses particular challenges for the professional scientists coordinating such research. Knowledge about the structure of these projects, the research activities conducted by citizen scientists, and quality control of data collected by volunteers is essential to identify their contribution to marine science. We examined 227 published studies in which professional scientists collaborated with volunteers in a wide range of marine investigations. Most studies focused on a diverse assemblage of animals, followed by flora and other topics (e.g., contamination or beach dynamics). Seabirds, marine mammals, turtles, and fishes were the most commonly studied animals, but several studies also dealt with marine invertebrates. Many of the studied taxa were commercially important, emblematic, or endangered species. Surveys of invasive species took advantage of the extensive spatial scale that can be covered by large numbers of volunteers. as would be expected, the research activities of citizen scientists were concentrated in easily accessible coastal habitats, including sandy beaches, estuaries, coral reefs, and seagrass beds. Hot spots of marine citizen science projects (CSPs) were found not only in North america and Europe, but also in the Indo-West Pacific region. Contributions made by citizen scientists were equally based on incidental observations as on standardized surveys. Some of the research projects had been active for more than a decade, but most were midterm programmes, last-ing a few years or less. Volunteer participants came from a wide range of demographic backgrounds. usually, the participants were adults of both sexes, but a few studies considered either only men or only women (mainly in small fishing communities). Whereas several studies were based on school-children as volunteers, no study worked specifically with senior citizens. The educational level of participants, often not explicitly mentioned in the publications, was also diverse. Some projects selected participants based on their experiences, skills, or profession, but in the majority of the stud-ies, there was either no selection or no information was provided, suggesting that any interested citi-zen could participate. The preparation of participants ranged from brief written or oral instructions to extensive (weeks) training sessions with professional experts. In general, training effort increased with the complexity of the tasks conducted by volunteers, a crucial element being the adjustment MaRTIN THIEl ET al. 258 of simple methodologies to the capabilities of participants. Studies for which volunteers needed to identify many different species and estimate their abundances were considered the most complex tasks, and subsequent analysis of such studies by professional scientists must consider inherent bias or shortcomings. about half of the examined studies included some type of quality control to ensure that the data collected by citizen scientists met the standards of rigorous scientific studies. Several authors emphasized that data quality increased with the duration of project participation. Efforts therefore should be made to retain experienced volunteers over time, which is facilitated when volunteers perceive that their efforts lead to something of practical use, such as publications, conservation initiatives, management decisions, or policy actions. Participants seemed to value personal satisfaction and public recognition, but learning about the ocean was also important. The coordinators of marine CSPs often collaborated with organizations such as conservation groups, birdwatchers, dive associations, or fishermen's cooperatives to recruit volunteers, but media cam-paigns, personal communication, social media, and functional websites were also important. Some studies were based on small numbers of participants (e.g., artisanal fishermen); others involved thou-sands of volunteers (e.g., coral or litter surveys). Volunteer-generated data contributed information about population dynamics, health, or distribution of marine organisms and supported long-term monitoring programmes of marine protected areas, harmful algal blooms, or marine litter, among others. In general, the contribution of citizen scientists greatly enhances research capacity, provid-ing an increased workforce over extensive spatial and intensive temporal scales at comparatively moderate costs. Citizen science is able to make significant contributions to marine science, where professional scientific activities are limited by the available human resources. Considering the vast-ness of the oceans and the diversity of habitats, communities, and species, proper understanding of this realm requires intensive research activities over time and space. This recognition should lead to increased consideration of citizen science as a powerful tool for the generation and spread of scien-tific knowledge. Furthermore, sharing knowledge between volunteer participants and professional scientists improves communication, trust, and capacity building, facilitating efficient collaboration in much-needed conservation initiatives.
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The coastal waters surrounding Britain and Ireland became warmer during the 20th century and, according to the UK Climate Impact Programme 2002 scenarios of change and other sources, average annual seawater temperatures may rise a further 2°C or more by the 2050s. This warming is part of a global rise in sea‐ and air‐surface temperatures that will cause changes in the distribution and abundance of species. Initially, there will not be a wholesale movement northwards of southern species or retreat northwards of northern species, because many additional factors will influence the responses of the different organisms. Such factors include the hydrodynamic characteristics of water masses, the presence of hydrographical and geographical barriers to spread and the life history characteristics (reproductive mode, dispersal capability and longevity) of species. Survey data over the past century show how organisms react to changes of the order of 0.5°C, and in the last two decades, when sea temperatures have risen by as much as 1°C, there have been significant local changes in the distribution of intertidal organisms. These past changes provide a clue to more extensive changes expected in the future if global warming develops as predicted. Where species affected by climate change are dominant or key structural or functional species in biotopes, there may be a change in the extent and distribution of those biotopes. Some, dominated by predominantly northern species such as the horse mussel Modiolus modiolus , may decline and reduce their value as rich habitats for marine life. Others, characterized by southern species, for example the sea fan Eunicella verrucosa and the alcyonacean Alcyonium glomeratum , may increase in extent. Using information on the life history characteristics of species, their present distribution and other factors, a key supported by a decision tree has been constructed to identify ‘types’ of organism according to their likely response to temperature rise. Conspicuous and easily identified rocky substratum species are good candidates to track change. Using the key, many species are shown as likely to increase their range northwards significantly. In contrast, fewer will decline in abundance and extent in the north. If, as anticipated, global warming continues, then species with distributions already accurately mapped, or being mapped at present, will provide baseline data to test forecasts. Copyright © 2004 John Wiley & Sons, Ltd.